生化抑制剂组合对黄泥田土壤氨挥发及累积特性的影响

采用室内培养方法,通过不同剂量和配比试验,研究脲酶抑制剂N-丁基硫代磷酰三胺(NBPT)、硝化抑制剂2-氯-6-(三氯甲基)吡啶(CP)及其两者组合对黄泥田土壤氨(NH3)挥发速率、累积特征及动力学特性的影响。结果表明:尿素施用于黄泥田土壤后3天NH3挥发速率逐渐到达峰值,随后下降趋于平稳;与单施尿素处理相比,不同剂量CP处理会加剧土壤中NH3挥发,增加NH3挥发速率峰值10.9%;不同剂量NBPT处理延缓土壤中NH3挥发出峰时间,显著降低NH3挥发速率峰值35.0%;培养第24天,NBPT处理土壤NH3挥发累积量较单施尿素处理降低37.2%,而CP处理增加2.1%;NBPT抑制黄泥田土壤NH3挥发效果显著;与仅添加CP处理相比,两者组合表现出有效地对NH3挥发损失的协同抑制效应;NBPT+CP组合可以有效延缓施肥初期尿素水解,从而减少NH3挥发损失;土壤NH3挥发累积量(第24天)较单施尿素处理降低14.2%,而随着CP剂量的增加,损失量增大;NH3挥发累积量随时间(t)变化的动力学特性可用Elovich方程(qt=a+blnt)进行定量描述,且拟合值显著相关;其中,CP处理增加斜率b值,且随着剂量的增加而增大;NBPT处理降低斜率b值,且随着剂量的增加而减小;NBPT+CP组合可以有效降低斜率b值。相关性分析表明,黄泥田土壤中NH3挥发速率与pH值呈显著正相关。总体认为,在黄泥田土壤中施用NBPT,或与CP配施可以显著减少土壤NH3挥发损失量,降低土壤氮素损失,提高肥料利用率。     

施用南荻生物炭对不同类型土壤氨挥发的影响

在洞庭湖区农田施用秸秆生物炭不仅能实现秸秆资源化利用,还可降低环境污染压力。本研究于2020年采用水稻盆栽试验,研究了不同南荻秸秆生物炭施用量对土壤氨挥发速率、累积氨挥发量、表面水pH值和NH₄⁺-N浓度的影响。供试土壤为第四纪红土发育的红黄泥和花岗岩发育的麻砂泥水稻土,设置6个南荻秸秆生物炭添加处理,即分别以土柱0～20 cm土壤重量的0%、1%、2%、4%、6%和8%比例添加生物炭,每盆施用复合肥200 kg N·hm^-2。结果表明: 施用生物炭导致两种土壤之间或不同生物炭处理之间的氨挥发速率和累积量均存在显著差异。麻砂泥施用生物炭处理在施肥后第2天出现氨挥发峰值,且较不施生物炭处理峰值降低了23.6%～53.4%;红黄泥氨挥发峰值出现在施肥后第7～13天,且其峰值随着生物炭添加量的增加而升高。整体上,麻砂泥土壤的氨挥发速率均高于红黄泥。麻砂泥土壤＜4%生物炭添加量能抑制土壤氨挥发速率及累积量,其中以2%处理降幅最大(46.9%),但生物炭添加对水稻生长前期表面水pH值的影响不显著;红黄泥土壤随着南荻生物炭用量的增加,表面水中pH值和NH₄⁺-N浓度增加,导致氨挥发速率及累积量增幅达1.3～10.5倍。回归分析显示,生物炭添加量是影响两种土壤氨挥发的关键因素。Elo-vich方程能较好地拟合两种土壤的氨挥发累积量随时间的变化动态,各施炭处理的相关系数均达极显著水平。总体上,对于偏中性的麻砂泥土壤,施用一定量的南荻生物炭对氨排放有一定的抑制作用,而对于酸性的红黄泥土壤,增施南荻生物炭会通过提高表面水的pH值和NH₄⁺-N浓度促进氨挥发,因此针对不同类型土壤施用南荻秸秆生物炭应注意选择适宜用量,以降低氮素损失。     

几种控释氮肥减少氨挥发的效果及影响因素研究

采用“静态吸收法”和“土柱淋溶法”、室内模拟试验,研究几种控释氮肥施入土壤后的氨挥发损失情况、N溶出速率、土壤脲酶活性及pH值变化的关系．结果表明,施氮450mg·kg^-1土时,3种控释氮肥氨挥发损失氮总量分别比普通尿素减少49．7％、28．0％和71．2％;施氮600mg·kg^-1土时,3种控释氮肥氨挥发损失氮总量分别比普通尿素减少34．6％、12．3％和69．9％．控释氮肥能显著降低土壤氨挥发量,减少因施肥而引起的大气环境污染．控释氮肥氨挥发量与不同氮肥引起的土壤脲酶活性、pH值、土壤中氮溶出速率密切相关．土壤的氨挥发总量与肥料在土壤中溶出总量的相关系数达到0．9533,在肥料施入的前期土壤氨挥发量同土壤脲酶活性、pH值的相关系数达到0．9533和0．9908。     

不同尿素配施处理下土壤氨挥发特性

采用室内恒温模拟培养方法,以单施尿素处理为对照,研究了减量尿素配施玉米秸秆、配施脲酶抑制剂NBPT和硝化抑制剂DMPP组合、配施玉米秸秆+抑制剂组合等处理对棕壤氨挥发特性的影响,分析了不同处理土壤的p H、铵态氮、硝态氮含量与氨挥发速率的相关性。结果表明:单施尿素处理氨挥发速率在第3天即达到峰值;减量尿素配施玉米秸秆处理的氨挥发速率峰值出现时间延迟至施肥后第5天;在配施玉米秸秆的土壤中添加抑制剂组合后,氨挥发速率峰值延迟至第11天出现。与单施尿素相比,减量尿素配施玉米秸秆并添加抑制剂组合可显著降低氨挥发速率峰值74.27%,培养18 d可减少氨挥发累积损失量43.96%。不同处理的氨挥发速率与土壤的铵态氮浓度、p H呈正相关,与土壤的硝态氮浓度呈负相关。配施玉米秸秆并添加抑制剂组合的土壤中铵态氮浓度达到高峰后可长时间保持较高水平(350 mg·kg-1),并可有效减少硝态氮的浓度。     

不同包膜控释尿素对农田土壤氨挥发的影响

为了探索包膜控释尿素土壤氨挥发损失规律特征和提高肥料氮素利用率,采用小麦玉米轮作田间试验,通过与普通尿素进行对比,运用土壤氨挥发原位测定方法——通气法系统研究了硫包膜和树脂包膜控释尿素的施用对小麦玉米轮作农田土壤氨挥发的影响.研究结果表明:在两种施氮量水平下(210 kg/hm2和300 kg/hm2),与普通尿素相比,硫包膜和树脂包膜控释尿素在小麦基肥期、小麦追肥期和玉米施肥期的施用均减少了土壤氨挥发的累积损失量,分别达35.1％-54.3％、59.6％-75.2％、65.6％-98.1％;有效降低了土壤氨挥发通量峰值且延迟其出现时间3-8 d,并能延缓土壤氨挥发主要阶段的时间分别为4-12 d、5-12 d.在小麦玉米轮作周年中,控释尿素土壤氨挥发累积损失量为28.39-43.35 kg/hm2,土壤氨挥发损失率为4.48％-5.63％,控释尿素时段土壤氨挥发通量比普通尿素降低了51.0％-70.8％;且树脂包膜控释尿素的施用降低小麦玉米轮作农田土壤氨挥发的效果优于硫包膜控释尿素.     

曝气充氧条件下污染河道氨挥发特性模拟

以污染河道为研究对象,模拟研究污染河道在曝气充氧(底泥曝气,ES组;水曝气,EW组)条件下氨挥发的特性,探讨主要影响因素及其作用过程.研究表明,污染河道水体具有一定氨挥发潜力,在实验室模拟条件下,氨挥发速率平均为2.51mg·m-2·h-1,相当于0.50 kgN· hm-2·d-1;曝气污染河道水体的氨挥发有一定的促进作用,与对照相比(EC组)氨挥发速率和累积氨挥发量存在显著差异(P＜ 0.05);不同曝气方式对氨挥发过程影响不同,氨挥发速率存在显著差异(P＜0.05);至实验结束,EW组的累积挥发量为2809.76 mg/m2,分别是ES组和EC组的1.17和2.25倍;各实验组的氨挥发累积量用一级动力学方程能很好地拟合,根据模型可以预测氨挥发量;同一温度条件下,pH值、铵氮浓度和通气频率是影响氨挥发的主要因素;曝气可以通过增加通气频率和提高水体pH值来促进氨挥发进行;在曝气作用下随着硝化过程的进行对氨挥发有一定的限制作用;曝气条件下,氨挥发作用在硝化过程启动阶段最为明显.     

日光温室番茄-西瓜轮作系统不同水氮处理氨挥发特征

为探究黄土高原地区日光温室果蔬栽培中氨挥发特征,在陕西省杨凌区选择当地典型的日光温室,设置4个不同的水氮处理,采用密闭式间歇抽气法监测番茄-西瓜轮作季的氨挥发特征.结果表明: 日光温室栽培土壤氮素转化快,施氮处理施肥后第1～2天氨挥发出现峰值,氨挥发峰值为0.26～2.02 kg N·hm^-2·d^-1,7 d左右各处理氨挥发通量相近;施氮处理间氨累积排放量无显著差异;相同施氮量条件下,降低灌溉量氨累积排放量两季平均增加了46.7%;不同种植季氨平均排放通量和累积排放量均表现为西瓜季高于番茄季,西瓜季高温促进了氨排放;土壤铵态氮含量、土壤孔隙含水量、0～5 cm地温和温室气温均对氨排放通量有极显著影响,而土壤pH值与氨挥发通量呈显著负相关关系.不同种植季氨挥发通量和累积排放量存在差异,降低施氮量可减少氨排放,相同施氮量条件下降低灌溉量增加了氨排放.     

不同施肥与灌水量对槟榔土壤氨挥发的影响

利用通气法田间原位试验,研究了不同施肥模式、灌溉量对槟榔土壤氨挥发速率和挥发量的影响。结果表明：槟榔恢复期和出花期追肥灌水后,不同施肥处理均在第3天出现氨挥发速率峰值（0.50-3.42 kg.hm-2.d-1）,而后迅速下降并进入低挥发阶段。出花期氨挥发速率峰值（1.50-4.42 kg.hm-2.d-1）比恢复期氨挥发速率峰值明显高。灌水量小(300 m3. hm-2)的氨挥发率和总量比灌水量大(600 m3. hm-2)的明显减小。在同一氮水平下,有机质含量较低的氨挥发率较高。在同一有机质含量条件,氨挥发率随着N肥含量增加而升高。与单施N肥处理相比,有机肥与N肥配施可明显减少氨挥发速率和总量,可减少氮损失。     

基于氮同位素标记技术的高寒人工草地氮肥氨挥发和氮素回收率研究

通过野外原位试验, 采用¹⁵N 标记技术和密闭室间歇通气法, 在青海省同德牧场高寒燕麦人工草地研究不施肥对照、单施尿素、尿素+脲酶抑制剂(NBPT)、尿素+硝化抑制剂(DMPP)、尿素+NBPT+DMPP 处理下高寒人工草地氨挥发、草地初级生产力及15N 标记肥料在牧草茎叶、根系和土壤中的回收率, 为高寒草地生态系统管理和可持续利用模式提供科学依据。结果表明: (1)不同处理下高寒人工草地土壤氨挥发速率表现为: 不施尿素对照处理总体上处于较低且稳定的水平(4.13-7.11g N·hm^-2·d^-1); 单施尿素处理氨挥发速率第2 天达到最大值343.43 g N·hm^-2·d^-1, 随后逐渐下降; 尿素+DMPP 处理氨挥发速率第2 天达到最大值216.53 g N·hm^-2·d^-1; 尿素+NBPT 和尿素+NBPT +DMPP 处理氨挥发速率均在第7 天达到最大值, 分别为43.19 g N·hm^-2·d^-1、34.55 g N·hm^-2·d^-1。(2)不同处理下高寒人工草地土壤累计氨挥发量表现为: 尿素(727.77 g N·hm^-2)> 尿素+DMPP(439.30 g N·hm^-2)> 尿素+NBPT(94.85 g N·hm^-2)> 尿素+NBPT+DMPP(80.01 g N·hm^-2)。统计结果表明, 除尿素+NBPT+DMPP 和尿素+NBPT 之间差异不显著外, 其余处理间累计氨挥发量差异显著(P<0.05)。(3)不同处理下高寒人工草地总初级生产力表现为: 不施肥对照处理总初级生产力为565.57 g·m^-2·y^-1,施尿素处理总初级生产力为652.36 g·m^-2·y^-1, 尿素+DMPP、尿素+NBPT、尿素+NBPT+DMPP 处理总初级生产力为678.33-704.41 g·m^-2·y^-1。(4)不同处理下高寒人工草地¹⁵N 肥料在牧草茎叶、根系和土壤中的回收率看: 单施尿素处理15N 总回收率(茎叶+土壤+根系)为57.67%, 尿素+DMPP 处理¹⁵N 总回收率为58.08%, 尿素+NBPT、尿素+NBPT+DMPP 处理¹⁵N 总回收率分别为68.74%和79.82%。统计结果显示尿素+NBPT+DMPP 和尿素+NBPT 处理显著提高高寒人工草地氮肥回收率。另外, ¹⁵N 标记肥料在牧草茎叶的回收率为28.45%-37.62%, 在牧草根系中的回收率为2.33%-2.68%, 土壤层(0-0 cm)中回收率为25.90%-41.64%。可以看出, 尿素+NBPT+DMPP 与尿素+NBPT 是同德高寒人工草地降低氨挥发和提高氮肥利用率的最佳施肥措施。     

施用坡缕石对黄绵土中尿素氮的挥发和淋溶损失的影响

通过室内模拟试验,采用吸收法和土柱淋溶法研究了施用坡缕石对黄绵土中尿素氮的挥发和淋溶的影响.结果表明：施用坡缕石+尿素处理能降低尿素氨挥发高峰期的挥发速率,比单施尿素处理的氨挥发损失减少了13.6%～15.0%.坡缕石施用量为0.3和0.6 g·kg^-1时,降低了NH₄⁺-N和NO₃^--N的淋溶速率,无机氮淋溶损失比单施尿素处理分别减少13.7%和13.6%;而坡缕石施用量为0.9 g·kg^-1时,加快了NH₄⁺-N和NO₃^--N的淋溶速率,无机氮淋溶损失比单施尿素处理增加了6.1%.施用低量（0.3 g·kg^-1）坡缕石+尿素处理土壤的NH₄⁺-N含量比单施尿素处理提高了0.20 mg·kg^-1,而施用高量（0.9 g·kg^-1）坡缕石+尿素处理土壤的NH₄⁺-N含量比单施尿素处理降低了0.42 mg·kg^-1;施用坡缕石+尿素处理土壤的NO₃^--N含量比单施尿素处理增加1.24～2.52 mg·kg^-1.表明施用坡缕石能减少土壤中尿素氨的挥发损失,在一定用量范围内能降低NH₄⁺-N和NO₃^--N的淋失,提高土壤NH₄⁺-N和NO₃^--N含量.     

Effect of phenylphosphorodiamidate on urea hydrolysis,ammonia volatilization and rice growth in an alkali soil

Summary In order to improve nitrogen recovery by rice, the effect of a urease inhibitor phenylphosphorodiamidate (PPD) on the efficiency of fertilizer urea was studied in laboratory and greenhouse. Addition of PPD to urea (5% w/w) delayed urea hydrolysis by 3 to 4 days and reduced ammonia volatilization from 45% (without PPD) to 8.5% (with PPD). Ammonia volatilization obeyed first order kinetics. Urea hydrolysis was sufficiently strongly inhibited to match the nitrification potential of the soil. N application to rice by three different modes showed that a delayed mode (4 splits) was superior to two conventional modes (3 splits) in nitrogen recovery and fertilizer efficiency since it met nitrogen requirement of plants at reproductive stage. In 2 out of 3 modes of application, there was a 14% increase (relative) in grain yields and dry matter, and 6.8% increase in N uptake efficiency on application of PPD along with urea. The results indicate that urease inhibitors like PPD can be effectively used to block urea hydrolysis, reduce ammonia volatilization losses and improve N use efficiency by rice.     

Effects of a slow-release urea source on absorption of ammonia and endogenous production of urea by cattle

Three experiments were conducted with Angus or Holstein steers to evaluate effects of dietary urea–calcium (a slow rumen-release urea source) on absorption of ammonia N from the gut and urea N production in the liver. Steers were fed a high-grain diet (Experiment 1) or an all-forage diet (Experiments 2 and 3). Urea or urea–calcium (0.25 g/kg body weight) was dosed into the esophagus (Experiments 1 and 2) or rumen (Experiment 3), and blood samples were serially collected for 180 min. Blood concentrations of ammonia N and urea N were measured in all experiments, and net flux of metabolites across splanchnic tissues was measured in Experiment 3. Compared to urea, urea–calcium reduced (P<0.05) plasma concentrations of ammonia N in steers fed all-forage diets, and tended (P<0.06) to reduce arterial glucose concentrations in Experiment 3. Plasma concentrations of urea N were not affected by treatment in any experiment. Treatment and time post-dosing interactions (P<0.05) in Experiment 3 were due to increased ruminal fluid concentrations of ammonia N, net release of ammonia N by portal-drained viscera and total splanchnic tissues with urea versus urea–calcium treatment shortly after dosing. Similar interactions (P<0.05) indicated that urea caused higher hepatic glucose release and increased l-lactate release by total splanchnic tissues after dosing than urea–calcium. Urea–calcium was effective in mitigating rapid ammonia release in the rumen and subsequent effects on glucose and lactate metabolism.     

Labeled nitrogen fertilizer research with urea in the semi-arid tropics

Summary Field studies with bordered microplots were conducted on an Alfisol in the semiarid tropics of India to determine (1) the fate of¹⁵N-labeled urea applied to dryland sorghum in two successive rainy seasons and (2) the effect of method of application on N fertilizer efficiency. Recoveries of¹⁵N-labeled fertilizers by above-ground plant parts ranged from 46.7% to 63.6% in 1981 when the rainfall was above the average and from 54.4% to 66.9% in 1980 when the rainfall was near the average. Small (0.014 g) pellets of urea applied twice as postemergent applications in separate 5 cm deep bands were more effective than single preemergent applications either surface applied or incorporated. Both banding and the split applications contributed to overall fertilizer efficiency. Large (1.0 g) pellets of urea (supergranules) placed at a depth of 5 cm were also superior to the incorporated, small-pellet treatment in 1981. The¹⁵N-balance data for the soil (0–90 cm in depth)-plant system in 1981 showed that the unaccounted-for fertilizer N ranged from 5.1% to 20.6%. An important finding was that high grain yields, in excess of 6,000 kg/ha, with N fertilizer losses of less than 10% could be obtained through fertilizer management during a very wet season. The data from the Alfisol experiments were compared with data from similar Vertisol experiments; N fertilizer losses resulting from incorporated and surface applications were greater for Vertisols than for Alfisols in the wetter year.     

尿素施用量对小麦根际土壤微生物数量及土壤酶活性的影响

在大田高产条件下,研究了不同尿素施用量下两种不同穗型小麦品种“兰考矮早8”和“豫麦49—198”根际微生物数量和土壤酶活性的变化。结果表明：微生物数量随小麦生育时期的进行呈规律性变化,其中微生物总量在拔节期和抽穗期时数量较多。尿素施用量对小麦根际微生物数量和酶活性均产生一定的影响,并且处理间差异达到显著水平。两个小麦品种根际微生物总量、细菌、放线菌、真菌数量随着尿素施用量的增加呈先上升后下降的趋势,但两个品种根际微生物数量最高时的尿素量略有差异。同一生育时期,随着尿素施用量的提高,土壤蛋白酶、过氧化氢酶呈先增加后降低的变化趋势,以他（391kg／hm^2）或T3（586kg／hm^2）处理的酶活性较高,T4（782kg／hm^2）处理的酶活性略有降低;脲酶活性则呈上升趋势,以T4（782kg／hm^2）处理的脲酶活性最大。表明适宜尿素施用量有益于小麦根际微生物数量和酶活性的提高,过高则微生物数量和酶活性下降。     

Effect of urea placement on leaching losses of nitrogen from flooded rice soils

In an effort to provide an explanation for the reported variability in fertilizer N efficiency from deepplaced urea on flooded rice, a set of controlled experiments was conducted to evaluate the effect of water percolation on fertilizer loss and plant uptake from¹⁵N labeled urea supergranules. Three soils of different texture (silt loam-clay) were subjected to various percolation rates (0–20 mm/day) while planted to rice which was harvested after approximately 40 days.The results indicate that moderate to high percolation through silt loam soil will lead to significant fertilizer N losses and drastically decrease the fertilizer uptake by plants. The permeability of the clay soil was too low for any leaching to take place. It is therefore concluded that deep placement of urea supergranules not be recommended in soils where percolation rates may exceed 5 mm/day, particularly if the cation exchange capacity of the soil is low. This experiment points to the need of evaluating and reporting the percolation rates in soils where experiments with supergranular urea are conducted.Contribution from the Agro-Economic Division of the International Fertilizer Development Center (IFDC), Muscle Shoals, Alabama 35660.     

Urea hydrolysis and transformations in coastal dune sands and soil

Summary Urea hydrolysis was studied in samples taken from a coastal sand dune succession, from uncolonized sand; the rhizosphere ofAmmophila arenaria and soil from the mature dune. Comparisons were made with urea hydrolysis in a fertile loam soil. Urea was hydrolyzed in all sand and soil samples, with complete hydrolysis occurring after 6 and 3 weeks in the rhizosphere sand and dune soil compared with only 4 days in the fertile loam. A third of the added urea, however, was still present in the uncolonized sand samples 6 weeks after the beginning of the incubation period. Urea hydrolysis broadly correlated with urease activity.The liberated NH ₄ ⁺ was oxidized to NO ₃ ^– –N in all samples. Urea stimulated the release of N from native organic matter in the two soils, but not sands, due presumably to the low organic matter content of the latter. Nitrite accumulated in the dune sands and soil, but not in the fertile loam.Although N-Serve (Nitrapyrin) had no effect on urea hydrolysis in any of the treated samples, it inhibited the nitrification of released NH ₄ ⁺ –N. The relevance of these findings to the use of urea as a fertilizer to improve plant growth and dune stabilization is commented upon.     

Labeled nitrogen fertilizer research with urea in the semi-arid tropics

Summary As part of a research program to determine the fate of N fertilizers applied to dryland sorghum in the semi-arid tropics,¹⁵N balance studies were conducted with various N sources in the greenhouse. Two American soils, Houston Black clay (Udic Pellustert) and Windthorst sandy loam (Udic Paleustalf), similar in properties to the Vertisol and Alfisol in the semi-arid tropics of India, were employed. Experiments were conducted with large pots containing 20 or 60 kg of soil which was subjected to several watering regimes. The¹⁵N not accounted for in the plant and soil was presumably lost. Losses of N on calcareous Houston Black clay were greatest for broadcast urea, 16%–28%. Amendment of broadcast urea with 2% phenyl phosphorodiamidate, a urease inhibitor, reduced N losses only slightly to 15%–20%. Point placement of urea at a 6 cm soil depth reduced losses to 1%–11%. Granule size had no effect on N loss from point-placed urea. Ammonia volatilization was apparently the main N loss mechanism, since N losses from sodium nitrate were less than 7%, except when the soil surface was waterlogged. N losses on the Windthorst soil averaged 30% from urea and 11% from ammonium nitrate. Amendment of urea with urea phosphate to form a 27% N and 13% P product reduced fertilizer N losses but did not increase grain yield on Windthorst soil. N losses were also less from ammonium nitrophosphate than from urea. Band and point placement of urea 6 cm below the soil surface were equally effective in reducing N loss on Houston Black clay. The findings give credence to the recommendation of deep band placement for urea in the semi-arid tropics.     

Uptake and use patterns of nitrogen from urea,oxamide, and isobutylidene diurea by rice plants

Summary Two¹⁵N-labelled slow-release nitrogen (N) sources, oxamide and isobutylidene diurea (IBDU), each at two particle sizes, and¹⁵N-labelled urea were compared at two rates as sources of N for rice (Oryza sativa) under two watering regimes which simulated a transplant (continuous flood, CF) and a direct-seeded (A/F) system of paddy rice culture. Highest grain yields were obtained from −8+10-mesh oxamide particles applied at the rate of 2,000 mg of N/5 kg of soil, CF series; this yield was slightly higher than that obtained from −3+4-mesh oxamide, A/F series. Incubating the N fertilizers in moist (22% water) soil for 21 days immediately before flooding and transplanting rice greatly reduced N supply because of nitrification during the preflood period, followed by denitrification after flooding. This resulted in less plant uptake of N and less grain yield from urea, fine oxamide and IBDU, A/F series. For coarse oxamide, N release during the preflood period resulted in higher N uptake and grain yield in the A/F rather than in the corresponding CF series. The pattern of fertilizer N uptake by rice plants was affected by kind of fertilizer, particle size of oxamide and IBDU, and watering regime. Uptake of fertilizer N generally paralleled uptake of soil N throughout the growth period. Plant tops continued to accumulate some N during the period of grain filling, but much of the N in plant tops was translocated to the grain after heading. There was a large decrease in dry weight, N content, and¹⁵N content of tops after heading. Root weight and N content increased rapidly at first, and then at a diminishing rate until maturity. Unexplained N deficits occurred in the CF series (14–23% of the N applied, depending on N rate and source), and in the A/F series for IBDU (37–43% of the N applied).     

Effects of parathion and malathion on transformations of urea and ammonium sulfate nitrogen in soils

Summary A study of the effects of malathion and parathion applied at 10 and 50 g/g of soil on transformations of urea and (NH₄)₂SO₄–N in a sandy loam showed that the insecticides retarded urea hydrolysis as well as nitrification of urea and (NH₄)₂SO₄–N. At 50 parts/10⁶ rate of the insecticides, inhibition of urea hydrolysis ranged from 44 to 61% after 0.5 week and from 7 to 21% after 3 weeks of application. The insecticides inhibited the conversion of NH₄ ⁺ to NO₂ ^– without appreciably affecting the subsequent oxidation of NO₂ ^– to NO₃ ^– –N. This resulted in accumulation of higher amounts of NH₄ ⁺–N in soil samples treated with ammonium sulfate or urea N.The results suggest that transformations of urea and NH₄ ⁺ fertilizers in soils may be influenced by the amount of organophosphorus insecticide present and this may affect plant nutrition and fertilizer use.     

Methodology for concurrent determination of urea kinetics and the capture of recycled urea nitrogen by ruminal microbes in cattle

We measured the incorporation of recycled urea-nitrogen (N) by ruminal microbes, using five ruminally and duodenally fistulated steers (237 kg) fed low-quality grass hay (47 g crude protein/kg dry matter (DM)). Three received 1 kg/day of soybean meal (SBM) and two received no supplemental protein (control). The experiment was 15 days long. Background enrichments of 15N were measured on day 9 and continuous jugular infusion of 0.12 g/day [15N15N]urea began on day 10. Daily samples of urine, feces, ruminal bacteria and duodenal digesta from days 10 through 14 were used to determine plateaus in 15N enrichment. Duodenal and bacterial samples collected on day 15 were used to measure duodenal N flows. Bacterial N flow was calculated as duodenal N flow multiplied by duodenal 15N enrichment divided by bacterial 15N enrichment. Bacterial N from recycled urea-N was calculated as bacterial N flow multiplied by bacterial 15N enrichment divided by urinary urea 15N enrichment. Urinary enrichment of [15N15N]urea plateaued within 24 h, whereas 14N15N urea plateaued within 48 h of [15N15N]urea infusion. Bacteria reached a plateau in 15N enrichment within 24 h and duodenal samples within 48 h. Urea production was 17.6 g of urea-N/day for control and 78.0 g/day for SBM. Gut entry was 0.99 g of urea-N/g of urea-N produced for control and 0.87 g/g for SBM. Incorporation of recycled N into microbial N was 9.0 g of N/day for control and 23.0 g/day for SBM. Recycled urea-N accounted for 0.33 g of N/g of microbial N at the duodenum for control and 0.27 g/g for SBM. Our methods allowed measurement of incorporation of recycled urea-N into ruminal microbial N.